BANNED A History of Pesticides and the Science of Toxicology Frederick Rowe Davis New Haven: Yale University Press, November 2014 |
Rating: 4.5 High |
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ISBN-13 978-0-300-20517-6 | ||||
ISBN-10 0-300-20517-1 | 264pp. | HC/BWI | $40.00 |
When I was in high school, my parents took me on vacations in the southern U.S. I remember well being in some North Carolina motel when the DDT foggers came through in the evening. I walked around in the mist as I unpacked the car. Little did I know then, in my early teens, that it was other than an unalloyed boon. (To be clear, I suffered no ill effects myself. But of course I had only a single brief exposure.)
Trained as a wildlife biologist, Rachel Carson began researching the effects of insecticides in the late 1950s. When Silent Spring was published in 1962, it caused a sensation: it became a best-seller and helped set the environmental movement in motion; but it also set the chemical industry and the U.S. Department of Agriculture against her. That animus lives on today, as a loud faction continues to blame her for crimes she never committed, even for things that never happened. A clearer view was expressed on her death by Senator Abraham Ribicoff during the Interagency Coordination on Environmental Hazards hearings at which she had testified.
"To the extent that Silent Spring brought the unintended consequences of chemical insecticides to the attention of Americans, Carson's testimony to the Ribicoff subcommittee on interagency coordination underscored the importance of the soft-spoken biologist in the quest to understand the risks of pesticides and helped to place their benefits in context, much like the CBS report a few weeks prior. Carson succumbed to cancer some ten months after appearing before the committee, but the hearings continued, and to mark the sad occasion Ribicoff read a tribute to Carson: 'After Rachel Carson brought her message of concern to the public, it was no longer possible to consider only the benefits of manmade pollution without weighing the risks. It was no longer possible to build a new factory without being concerned about air pollution, a nuclear reactor without being concerned about water pollution, or a new pesticide to make food more abundant without being concerned about the health of wildlife and even people. She was no fanatic, trying to wish away the advantages of the 20th century. She was a humanitarian, insisting that man weigh carefully the consequences of his modern technology and strike a balance that will preserve the wonder of nature in the 21st century.' Ribicoff concluded: 'Today we mourn a great lady. All mankind is in her debt.' " – Page 171 |
There has been much dispute over the worth of pesticides, primarily over DDT because of its unique history. Developed at Germany's I. G. Farben in 1937, it quickly became popular and — ironically for the Third Reich — proved a great boon to the Allied Powers in World War II, especially in the Italian campaign where it protected the troops from typhus.
"With the advent of World War II there was renewed interest in insecticides that could control the spread of malaria and other insect-borne diseases. DDT was the most promising of these, and its potential effects on target organisms, lab animals, wildlife, and humans underwent extensive analysis. [...] Such scrutiny demonstrated that DDT had opened a new era in insect control and toxicology. No other insecticide killed such a broad spectrum of insects without damaging the crops it was protecting. No other insecticide inspired such extensive investigation." – Page 91 |
After the War, DDT was produced in massive amounts by U.S. manufacturers. The manufacturers found ready markets in the agriculture industry, where DDT swiftly controlled all manner of crop pests with little apparent harm to humans or wildlife. But within a few years it became clear that DDT was having major impacts on wildlife populations where it was used. These impacts have been extensively documented. In the same period, medical doctors began to notice harm to humans. Damage to kidneys, liver, and the nervous system were discovered. Such damage required long-term exposure. But that is why DDT and the other insecticides in its class, the chlorinated hydrocarbons, are so insidious: they persist in the environment and collect in fatty tissues. Thus, those who eat fruit with DDT residue over a long period can suffer various kinds of chronic illness. However, getting a DDT preparation on your skin while applying it will do no harm as long as you wash it off promptly.
DDT's other problem is that many pests, including houseflies and mosquitoes, can rapidly become immune to its effects. So can the malaria parasite. Use of DDT was banned in the U.S. in 1972, after contentious congressional hearings where testimony revealed the newly discovered problems. It is still made here, and used in many places overseas. It is a genuine boon if applied properly. Unfortunately, many factors combine to impede proper use.
"Carson published Silent Spring at a critical moment in the history of environmental science. Studying her sources and rereading her careful interpretations of science deepens our appreciation of the achievement of Silent Spring. But an analysis of pesticides policy and usage policy in the decades following the ban on DDT exposes a tragic irony in the worldwide proliferation of the organophosphate pesticides, chemicals that Carson and the toxicologists acknowledged to be far more toxic to wildlife and humans alike." – Page xi |
This ban is doubly unfortunate because it has led to substitution of other, more dangerous pesticides for DDT. Chief among them are the organophosphates1 including parathion and monocrotophos.2 In the long battle with crop pests and vector-borne diseases like malaria, we have often wielded chemical weapons we did not really understand. Tragedies have resulted. But we do learn, in time. The author shows us the work of the toxicologists who gave us that understanding — a knowledge still incomplete, but improving. The declining uses of pesticides, as shown in the tables I provide below, are indications that we are growing wiser about pesticides.
"For the most part, organophosphate insecticides were not associated with carcenogenicity, so they passed through the screen that as the regulatory emphasis on cancer. Since they typically did not bioaccumulate in the environment, they avoided one of the chief drawbacks of the organochlorines. Lost in these toxicological analyses was the damage that organophosphate insecticides wrought to humans and wildlife directly in the form of acute toxicity. As we have seen, with the exception of malathion, organophosphates were moderately to highly toxic to humans and wildlife, especially birds, fish, aquatic organisms, and non-target insects, including bees. To a degree that would have shocked and disappointed Carson, the "road traveled" was flooded with highly toxic organophosphate insecticides, which she had identified as some of the most toxic chemicals known to man." – Page 209 |
Year of Use | |||||
---|---|---|---|---|---|
Pesticide | Class | 1966 | 1971 | 1976 | 1982 |
Based on Table 3 (Davis, pp. 204-205) | |||||
Acephate | OP | 0 | 0 | 588 | 1,137 |
Aldicarb | CB | 0 | 0 | 0 | 2,271 |
Aldrin | OC | 14,671 | 7,928 | 945 | 0 |
Azinphos-methyl | OP | 1,474 | 2,654 | 2,644 | 2,274 |
Carbaryl | CB | 12,392 | 17,838 | 15,829 | 9,984 |
Carbofuran | CB | 0 | 0 | 11,623 | 12,300 |
Chlordane | OC | 526 | 1,890 | 2,116 | 0 |
Chlorpyrifos | OP | 0 | 0 | 0 | 5,412 |
DDT | OC | 27,004 | 14,324 | 0 | 0 |
Diazinon | OP | 5,605 | 3,167 | 2,470 | 2,114 |
Dicrotophos | OP | 1,857 | 807 | 0 | 0 |
Dieldrin | OC | 724 | 0 | 0 | 0 |
Dimethoate | OP | 0 | 0 | 583 | 1,419 |
Disulfoton | OP | 1,952 | 4,079 | 6,873 | 2,443 |
Endosulfan | OC | 791 | 882 | 1,653 | 977 |
Endrin | OC | 751 | 1,427 | 866 | 0 |
EPN | OP | 0 | 0 | 6,249 | 1,373 |
Ethion | OP | 2,007 | 2,326 | 2,639 | 1,250 |
Ethyl Parathion | OP | 8,452 | 9,481 | 9,268 | 6,384 |
Ethoprop | OP | 0 | 0 | 0 | 2,907 |
Fensulfothion | OP | 0 | 0 | 748 | 0 |
Fenvalerate | SP | 0 | 0 | 0 | 1,273 |
Fonofos | OP | 0 | 0 | 5,008 | 5,486 |
Heptachlor | OC | 1,536 | 1,211 | 1,667 | 0 |
Lindane | OC | 704 | 650 | 0 | 0 |
Malathion | OP | 5,218 | 3,602 | 3,936 | 2,521 |
Methamidophos | OP | 0 | 0 | 0 | 942 |
Methomyl | CB | 0 | 0 | 3,417 | 4,353 |
Methoxychlor | OC | 2,578 | 3,012 | 4,057 | 0 |
Methyl Parathion | OP | 8,002 | 27,563 | 23,350 | 11,335 |
Mevinphos | OP | 0 | 0 | 0 | 1,277 |
Mexacarbate | OC | 502 | 0 | 0 | 0 |
Monocrotophos | OP | 0 | 0 | 1,917 | 761 |
Naled | OP | 0 | 0 | 0 | 745 |
Oil | N/A | 73,950 | 60,000 | 50,000 | |
Oxamyl | CB | 0 | 0 | 0 | 667 |
Paraffinic Oil | 11,419 | 0 | 0 | 0 | |
Permethrin | SP | 0 | 0 | 0 | 1,475 |
Phorate | OP | 0 | 0 | 6,957 | 5,379 |
Phosmet | OP | 0 | 0 | 523 | 903 |
Strobane | OC | 2,016 | 0 | 0 | 0 |
Sulprofos | OP | 0 | 0 | 0 | 749 |
TDE | OC | 2,896 | 0 | 0 | 0 |
Terbufos | OP | 0 | 0 | 2,492 | 8,632 |
Toxaphene | OC | 34,605 | 37,464 | 34,178 | 6,596 |
Trichlorfon | OP | 1,060 | 617 | 932 | 0 |
Year of Use | |||||
---|---|---|---|---|---|
Pesticide | Class | 1989 | 1992 | 1997 | 2002 |
Based on Table 4 (Davis, pp. 207-208) | |||||
Acephate | OP | 2,500 | 3,390 | 2,462 | 2,525 |
Aldicarb | CB | 5,317 | 4,022 | 4,278 | 3,419 |
Azinphos-methyl | OP | 3,000 | 2,549 | 2,091 | 1,224 |
Carbaryl | CB | 8,616 | 4,543 | 4,858 | 2,986 |
Carbofuran | CB | 7,156 | 5,101 | 3,398 | 1,015 |
Chlorpyrifos | OP | 11,300 | 14,765 | 13,464 | 8,481 |
Cryolite | FL | 0 | 4,053 | 2,560 | 1,102 |
Cypermethrin | SP | 500 | 0 | 0 | 0 |
Diazinon | OP | 1,847 | 1,266 | 918 | 858 |
Dicofol | OC | 0 | 1,392 | 787 | 0 |
Dicrotophos | OP | 550 | 666 | 0 | 0 |
Dimethoate | OP | 4,250 | 2,619 | 1,897 | 1,346 |
Disulfoton | OP | 2,023 | 1,807 | 1,196 | 0 |
Endosulfan | OC | 1,100 | 1,797 | 1,601 | 868 |
EPN | OP | 975 | 0 | 0 | 0 |
Esfenvalerate | SP | 500 | 0 | 0 | 0 |
Ethion | OP | 1,350 | 991 | 505 | 0 |
Ethoprop | OP | 2,500 | 1,450 | 1,011 | 0 |
Ethyl parathion | OP | 6,030 | 2,318 | 529 | 0 |
Fenamiphos | OP | 0 | 615 | 727 | 0 |
Fenvalerate | SP | 1,000 | 0 | 0 | 0 |
Fonofos | OP | 3,220 | 3,234 | 0 | 0 |
Kaolin | 0 | 0 | 0 | 1,690 | |
Malathion | OP | 6,327 | 3,378 | 5,810 | 5,132 |
Methamidophos | OP | 1,259 | 1,088 | 966 | 0 |
Methidathion | OP | 600 | 0 | 0 | 0 |
Methomyl | CB | 2,345 | 2,755 | 1,997 | 918 |
Methyl parathion | OP | 7,652 | 5,962 | 5,917 | 2,148 |
Mevinphos | OP | 757 | 0 | 0 | 0 |
Monocrotophos | OP | 550 | 0 | 0 | 0 |
Naled | OP | 600 | 0 | 605 | 0 |
Oil | 35,000 | 51,102 | 102,337 | 91,606 | |
Oxamyl | OP | 0 | 946 | 939 | 748 |
Permethrin | SP | 450 | 1,069 | 1,066 | 586 |
Phorate | OP | 5,329 | 4,453 | 3,218 | 1,197 |
Phosalone | OP | 750 | 0 | 0 | 0 |
Phosmet | OP | 1,000 | 941 | 1,333 | 0 |
Profenofos | OP | 777 | 2,063 | 880 | 0 |
Propargite | OS | 0 | 3,628 | 2,539 | 1,407 |
Sulfopros | OP | 0 | 852 | 0 | 0 |
Tebupirimphos | OP | 0 | 0 | 0 | 538 |
Tefluthrin | SP | 0 | 0 | 577 | 630 |
Terbufos | OP | 10,246 | 8,690 | 6,516 | 3,363 |
Thiodicarb | CB | 950 | 1,706 | 821 | 0 |
Trichlorfon | OP | 568 | 0 | 0 | 0 |
Year of Use | ||||||||
---|---|---|---|---|---|---|---|---|
Breakdown | 1966 | 1971 | 1976 | 1982 | 1989 | 1992 | 1997 | 2002 |
Derived from Tables 3 & 4 (Davis, pp. 204-208) | ||||||||
Pesticides in use | 24 | 24 | 29 | 31 | 36 | 32 | 31 | 24 |
Organochlorines in use | 12 | 9 | 7 | 2 | 1 | 2 | 2 | 1 |
Organophosphates in use | 9 | 10 | 18 | 21 | 25 | 22 | 20 | 14 |
Carbamates in use | 2 | 4 | 3 | 5 | 5 | 4 | 4 | 3 |
Synthetic Pyrethroids in use | 0 | 0 | 0 | 2 | 4 | 1 | 2 | 2 |
Year of Use | ||||||||
---|---|---|---|---|---|---|---|---|
Breakdown | 1966 | 1971 | 1976 | 1982 | 1989 | 1992 | 1997 | 2002 |
Derived from Tables 3 & 4 (Davis, pp. 204-208) | ||||||||
Qty. of Organochlorines in use | 88,892 | 68,788 | 45,482 | 7,573 | 1,100 | 3,189 | 2,388 | 868 |
Qty. of Organophosphates in use | 35,627 | 58,474 | 78,325 | 65,524 | 72,960 | 66,798 | 55,520 | 30,953 |
Qty. of Carbamates in use | 12,894 | 25,375 | 30,869 | 29,475 | 24,384 | 15,372 | 12,534 | 7,420 |
Qty. of Synthetic Pyrethroids in use | 0 | 0 | 0 | 2,748 | 2,450 | 1,069 | 1,643 | 1,216 |
Qty. of Organosulfonates (Propargite) in use | 0 | 0 | 0 | 0 | 0 | 3,628 | 2,539 | 1,407 |
Total Qty. of Pesticides in use | 137,413 | 152,637 | 154,676 | 105,320 | 100,894 | 90,056 | 74,624 | 41,864 |
Qty. of Cryolite in use | 0 | 0 | 0 | 0 | 0 | 4,053 | 0 | 0 |
Qty. of Kaolin in use | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1,690 |
Qty. of oil in use | 0 | 73,950 | 60,000 | 50,000 | 35,000 | 51,102 | 102,337 | 91,606 |
Qty. of Paraffinic oil in use | 11,419 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
"As Daniel, Langston, Oreskes and Conway, and Rosner and Markowitz and others have brilliantly demonstrated through numerous incisive examples, industry successfully captured regulatory agencies in the U.S. across the twentieth century to the detriment of the health and wellness of millions of Americans and others worldwide. In the case of pesticides, Daniel argued: "[USDA's Agricultural Research Service (ARS)] possessed enormous power, for its label approval function licensed pesticide formulations. It garnered enormous power in its multiple roles as clearinghouse, coordinator, regulator, and research center. To have their way, ARS bureaucrats bullied, plotted, lied, and misled. A culture emerged within the service that justified pesticides at all costs, and staffers bent research, reports, and testimony to serve this mission." – Pages 184-5 |